meta data for this page
Differences
This shows you the differences between two versions of the page.
| Both sides previous revisionPrevious revisionNext revision | Previous revision | ||
| sector:agriculture:manure_management:start [2026/02/11 10:13] – [Trend discussion for Key Sources] roesemann | sector:agriculture:manure_management:start [2026/03/16 15:28] (current) – [Table] mielke | ||
|---|---|---|---|
| Line 13: | Line 13: | ||
| | 3.B.4.g i-iv | Poultry | | 3.B.4.g i-iv | Poultry | ||
| | 3.B.4.h | | 3.B.4.h | ||
| + | | {{page> | ||
| ---- | ---- | ||
| - | ^ ^ NO< | + | ^ |
| - | | 3.B.1.a | + | | 3.B.1.a |
| - | | 3.B.1.b | + | | 3.B.1.b |
| - | | 3.B.2 | -/- | + | | 3.B.2 |
| - | | 3.B.3 | -/- | + | | 3.B.3 |
| - | | 3.B.4.d | + | | 3.B.4.d |
| - | | 3.B.4.e | + | | 3.B.4.e |
| - | | 3.B.4.g.i | + | | 3.B.4.g.i |
| - | | 3.B.4.g.ii | + | | 3.B.4.g.ii |
| - | | 3.B.4.g.iii | + | | 3.B.4.g.iii |
| - | | 3.B.4.g.iv | + | | 3.B.4.g.iv |
| + | | {{page> | ||
| - | | ||
| \\ | \\ | ||
| Line 95: | Line 96: | ||
| The data from the 2020 official agricultural census (DESTATIS, 2020)((Statistisches Bundesamt (2020): LW20, Landwirtschaftszählung 2020. https:// | The data from the 2020 official agricultural census (DESTATIS, 2020)((Statistisches Bundesamt (2020): LW20, Landwirtschaftszählung 2020. https:// | ||
| - | For a description of the RAUMIS data, the data from official surveys and additional data from other sources see Vos et al. (2026), Chapter 2.5. Time series of frequency distributions of housing systems, storage systems and application techniques as well as the corresponding emission factors are provided in NID 2026, Chapter 17.3.1. | + | For a description of the RAUMIS data, the data from official surveys and additional data from other sources see Vos et al. (2026), Chapter 2.5. Time series of frequency distributions of housing systems, storage systems and application techniques as well as the corresponding emission factors are provided in NID 2026((NID (2026): National Inventory Report 2026 for the German Greenhouse Gas Inventory 1990-2024. Available in April 2026.)), Chapter 17.3.1. |
| Since submission 2026 transports of manure, energy crops and digestates between NUTS 3 regions are simulated in the calculation model. This does not have major influence on the emissions of the whole country, but changes the distribution of emissions between single NUTS 3 regions. For details on the methodology, | Since submission 2026 transports of manure, energy crops and digestates between NUTS 3 regions are simulated in the calculation model. This does not have major influence on the emissions of the whole country, but changes the distribution of emissions between single NUTS 3 regions. For details on the methodology, | ||
| Line 149: | Line 150: | ||
| The calculation of the emissions of NH< | The calculation of the emissions of NH< | ||
| - | This approach differentiates between N excreted with faeces (organic nitrogen Norg, i. e. undigested feed N) and urine (total ammoniacal nitrogen TAN, i. e. fraction of feed N metabolized). The N flow within the manure management system is treated as depicted in the figure below. This method reconciles the requirements of both the Atmospheric Emission Inventory Guidebook for NH< | + | This approach differentiates between N excreted with faeces (organic nitrogen Norg, i. e. undigested feed N) and urine (total ammoniacal nitrogen TAN, i. e. fraction of feed N metabolized). The N flow within the manure management system is treated as depicted in the figure below. This method reconciles the requirements of both the Atmospheric Emission Inventory Guidebook for NH< |
| Not explicitly shown in the N mass flow scheme is air scrubbing in housing and anaerobic digestion of manure. These issues are separately described further below. Note that emissions from grazing and application are reported in sector 3.D. | Not explicitly shown in the N mass flow scheme is air scrubbing in housing and anaerobic digestion of manure. These issues are separately described further below. Note that emissions from grazing and application are reported in sector 3.D. | ||
| Line 181: | Line 182: | ||
| For the detailed emission factors of livestock husbandry see Vos et al. (2026), Chapter 4.3. | For the detailed emission factors of livestock husbandry see Vos et al. (2026), Chapter 4.3. | ||
| - | The detailed emission factors for N< | + | The detailed emission factors for N< |
| Table 3 shows the implied emission factors of NH< | Table 3 shows the implied emission factors of NH< | ||
| __Table 3: IEF for NH< | __Table 3: IEF for NH< | ||
| - | ^ ^ 1990 | + | ^ |
| ^ Ammonia | ^ Ammonia | ||
| ^ dairy cattle | ^ dairy cattle | ||
| Line 232: | Line 233: | ||
| All timeseries of the emission inventory have completely been recalculated. Tables 4 and 5 compare the recalculated time series for NH< | All timeseries of the emission inventory have completely been recalculated. Tables 4 and 5 compare the recalculated time series for NH< | ||
| - | For NH3 there are many reasons for very different emissions compared to last year’s submission. For dairy cows the new methodology to claculate N and TAN excretions (see main page of the agricultural sector **recalculation No. 3**) results in general in lower emissions. The upward correction of historic milk yields (**recalculation No. 4**) results in higher emissions. In combination these two recalculations result in lower emissions, especially in more recent years. The subdivision of the sows category in gilts and old sows (**recalculation No. 5**) is the main reason for lower emissions from swine. The adjusted N excretion for horses after 2010 (**recalculation No. 6**) is the main reason for higher emissions from other animals. The addition of substrate transports to biogas plants (**recalculation No. 1**) has a smaller impact on emissions than the other recalculations. This recalculation is the main reason for the changes for emissions from other cattle and poultry but it also affects dairy cattle and swine emissions. Many of the other recalculations have much smaller effects. Overall, the changes result in lower emissions compared with last year’s submission. | + | For NH3 there are many reasons for very different emissions compared to last year’s submission. For dairy cows the new methodology to claculate N and TAN excretions (see [[sector: |
| The total emissions of NO< | The total emissions of NO< | ||
| Line 240: | Line 241: | ||
| ^ NFR Total emissions | ^ NFR Total emissions | ||
| ^ ^ Submission | ^ ^ Submission | ||
| - | | Total ^ current | + | ^ Total ^ current |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | ::: ^ absolute change | + | ^ ::: ^ absolute change |
| - | | ::: ^ relative change [%] | -1.15 | -0.79 | -1.29 | -1.74 | -2.84 | -2.76 | -2.71 | -2.10 | -2.07 | -2.33 | -3.15 | -3.97 | -3.88 | -3.95 | | | + | ^ ::: ^ relative change [%] | -1.15 | -0.79 | -1.29 | -1.74 | -2.84 | -2.76 | -2.71 | -2.10 | -2.07 | -2.33 | -3.15 | -3.97 | -3.88 | -3.95 | | |
| - | | Dairy cattle | + | ^ Dairy cattle |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Other cattle | + | ^ Other cattle |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Swine ^ current | + | ^ Swine ^ current |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | poultry | + | ^ poultry |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Other animals | + | ^ Other animals |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| __Table 5: Comparison of NO< | __Table 5: Comparison of NO< | ||
| ^ NFR Total emissions | ^ NFR Total emissions | ||
| - | | ^ Submission | + | ^ ^ Submission |
| - | | Total ^ current | + | ^ Total ^ current |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | ::: ^ absolute change | + | ^ ::: ^ absolute change |
| - | | ::: ^ relative change [%] | 5.60 | 4.35 | 3.20 | 2.38 | 0.84 | 0.67 | 1.01 | 1.77 | 0.97 | 0.65 | -0.40 | -1.48 | -1.39 | -0.86 | | | + | ^ ::: ^ relative change [%] | 5.60 | 4.35 | 3.20 | 2.38 | 0.84 | 0.67 | 1.01 | 1.77 | 0.97 | 0.65 | -0.40 | -1.48 | -1.39 | -0.86 | | |
| - | | Dairy cattle | + | ^ Dairy cattle |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Other cattle | + | ^ Other cattle |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Swine ^ current | + | ^ Swine ^ current |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | poultry | + | ^ poultry |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Other animals | + | ^ Other animals |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| Line 333: | Line 334: | ||
| ^ NFR Total emissions | ^ NFR Total emissions | ||
| ^ ^ Submission | ^ ^ Submission | ||
| - | | Total ^ current | + | ^ Total ^ current |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | ::: ^ absolute change | + | ^ ::: ^ absolute change |
| - | | ::: ^ relative change [%] | 0.82 | + | ^ ::: ^ relative change [%] | 0.82 |
| - | | Dairy cattle | + | ^ Dairy cattle |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Other cattle | + | ^ Other cattle |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | Other animals | + | ^ Other animals |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| === Planned improvements === | === Planned improvements === | ||
| Line 423: | Line 424: | ||
| ==== Recalculations ==== | ==== Recalculations ==== | ||
| - | The following table 9 shows the effects of recalculations on emissions of particulate matter. | + | The following table 9 shows the effects of recalculations on emissions of particulate matter. |
| - | __Table 9: Comparison of particle emissions (TSP, PM< | + | __Table 9: Comparison of particle emissions (TSP, PM< |
| - | ^ TSP, PM< | + | ^ TSP, PM< |
| - | | ^ Submission | + | ^ ^ Submission |
| - | | TSP ^ current | + | ^ TSP ^ current |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | ::: ^ absolute change | + | ^ ::: ^ absolute change |
| - | | ::: ^ relative change [%] | 0.00 | 0.00 | 0.00 | 0.00 | -0.01 | -0.01 | -0.01 | 0.00 | 0.00 | 0.13 | 0.00 | 0.00 | 0.00 | 0.00 | + | ^ ::: ^ relative change [%] | 0.00 | 0.00 | 0.00 | 0.00 | -0.01 | -0.01 | -0.01 | 0.00 | 0.00 | 0.13 | 0.00 | 0.00 | 0.00 | 0.00 |
| - | | PM< | + | ^ PM< |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | ::: ^ absolute change | + | ^ ::: ^ absolute change |
| - | | ::: ^ relative change [%] | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.05 | 0.00 | 0.00 | 0.00 | 0.00 | | | + | ^ ::: ^ relative change [%] | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.05 | 0.00 | 0.00 | 0.00 | 0.00 | | |
| - | | PM< | + | ^ PM< |
| - | | ::: ^ previous | + | ^ ::: ^ previous |
| - | | ::: ^ absolute change | + | ^ ::: ^ absolute change |
| - | | ::: ^ relative change [%] | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.01 | 0.00 | 0.00 | 0.00 | 0.00 | | | + | ^ ::: ^ relative change [%] | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.00 | 0.01 | 0.00 | 0.00 | 0.00 | 0.00 | | |
| <WRAP center round info 65%> | <WRAP center round info 65%> | ||
| - | For **pollutant-specific information on recalculated emission estimates for Base Year and 2022**, please see the pollutant specific recalculation tables following [[general: | + | For **pollutant-specific information on recalculated emission estimates for Base Year and 2023**, please see the pollutant specific recalculation tables following [[general: |
| </ | </ | ||